Abstract

In ecological effects research, there is a rapid increase in the application of passive sampling techniques for measuring ambient ozone (O3) concentrations. Passive samplers provide data on cumulative exposures of a plant to a pollutant. However, O3 is not an accumulative contaminant within the plant tissue, and use of prolonged passive sampling durations cannot account for the dynamics of the occurrences of O3 that have a significant influence on the plant response. Therefore, a stochastic Weibull probability model was previously developed and applied to a site in Washington State (1650 m MSL) to simulate the cumulative exposure data from a passive sampler, to mimic the corresponding frequency distributions of hourly O3 concentrations that would otherwise have been obtained by continuous monitoring. At that site the correlation between the actual passive sampler and the continuous monitor data was R2 = 0.74. The simulation of the hourly O3 data was based on and compared with the results obtained from a colocated continuous monitor. In this paper we report the results of the model application to data from an unrelated monitoring site (New Hampshire, 476 m MSL) with poor correlation between the passive sampling and continuous monitoring (R2 = 0.24). In addition, as opposed to the previous work, we provide comparisons of the frequency distributions of the hourly O3 concentrations obtained by the simulation and the actual continuous monitoring. In spite of the major difference in the R2 values, at both sites the simulation provided very satisfactory results within the 95% confidence interval, suggesting its broad applicability. The final objective of this overall approach is to develop a generic model that can simulate reasonably well the occurrences of ambient O3 concentrations that are dependent upon the elevation of the measurement site and the synoptic and local meteorology. Such an effort would extend the relative utility of the passive sampling data in explaining stochastic plant responses.

Highlights

  • The use of passive ozone (O3) samplers in ecological effects research is increasing rapidly because they are easy to use and inexpensive, and they do not require electrical power

  • Cumulative exposures derived from prolonged sampling periods cannot account for the dynamics and flux of pollutant occurrences and the corresponding plant responses that are governed by the changing climatic patterns and physiological and growth characteristics of the plant species[5,6]

  • The overall results predicted by the Weibull model would have been even better if the variance of the measured passive sampler mean O3 concentrations had been less than what was observed, compared to the corresponding means from the colocated continuous monitor

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Summary

Introduction

The use of passive ozone (O3) samplers in ecological effects research is increasing rapidly because they are easy to use and inexpensive, and they do not require electrical power. Because of the aforementioned considerations, Krupa et al.[7] developed and verified a stochastic, Weibull probability model to simulate the underlying frequency distributions of hourly O3 concentrations (exposure dynamics) using the single, weekly mean values obtained from a passive (sodium nitrite absorbent) sampler.

Results
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